Food security entails having sufficient, safe, and nutritious food to meet dietary needs. The need to optimise nitrogen (N) use for nutrition security while minimising environmental risks in sub-Saharan Africa (SSA) is overdue. Challenges related to managing N use in SSA can be associated with both insufficient use and excessive loss, and thus the continent must address the ‘too little’ and ‘too much’ paradox. Too little N is used in food production (80% of countries have N deficiencies), which has led to chronic food insecurity and malnutrition.
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Library ResourceJournal Articles & BooksDecember, 2017Kenya, Rwanda, Uganda, Burundi, Tanzania, Africa, Eastern Africa, Middle Africa
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Library ResourcePolicy Papers & BriefsJanuary, 2016Rwanda, Middle Africa, Eastern Africa, Africa
The climate-smart agriculture (CSA) concept reflects
an ambition to improve the integration of agriculture
development and climate responsiveness. It aims to
achieve food security and broader development goals
under a changing climate and increasing food demand.
CSA initiatives sustainably increase productivity, enhance
resilience, and reduce/remove greenhouse gases (GHGs),
and require planning to address tradeoffs and synergies
between these three pillars: productivity, adaptation, -
Library ResourceReports & ResearchAugust, 2016Rwanda, Africa, Eastern Africa
Rwanda’s variable and changing climate is an increasingly serious challenge to the country’s
agricultural sector and farming population. Climate information services are emerging as a
means to support farmers to manage risk and provide an opportunity to build the resilience of
agriculture to climate at all time scales. Climate services include historical, monitored and
forecast information, and value-added information products such pest and disease risk
warnings, crop yield forecasts, or management advisories. The new Rwanda Climate Services
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Library ResourcePolicy Papers & BriefsNovember, 2016Rwanda, Africa, Sub-Saharan Africa
? The Rwanda Dairy Competitiveness Program II
(RDCP) was estimated to have resulted in a
strong decrease in the GHG emissions intensity
of milk production, defined as the GHG
emissions per unit (liter) of milk produced.
Extensive cattle production systems reduced
their GHG emission intensity by an estimated -
4.11 tCO2e per 1000 l of milk (-60%), while
intensive production systems reduced their
intensity by an estimated -1.7 tCO2e/1000 l (-
47%). The decrease in GHG emission intensity
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